JP3379125B2 - Exhaust gas purification catalyst - Google Patents

Exhaust gas purification catalyst

Info

Publication number
JP3379125B2
JP3379125B2 JP00249293A JP249293A JP3379125B2 JP 3379125 B2 JP3379125 B2 JP 3379125B2 JP 00249293 A JP00249293 A JP 00249293A JP 249293 A JP249293 A JP 249293A JP 3379125 B2 JP3379125 B2 JP 3379125B2
Authority
JP
Japan
Prior art keywords
exhaust gas
catalyst
lanthanum
gas purification
lean
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Expired - Lifetime
Application number
JP00249293A
Other languages
Japanese (ja)
Other versions
JPH06205975A (en
Inventor
直人 三好
高弘 林
伸一 松本
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Toyota Motor Corp
Original Assignee
Toyota Motor Corp
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Toyota Motor Corp filed Critical Toyota Motor Corp
Priority to JP00249293A priority Critical patent/JP3379125B2/en
Publication of JPH06205975A publication Critical patent/JPH06205975A/en
Application granted granted Critical
Publication of JP3379125B2 publication Critical patent/JP3379125B2/en
Anticipated expiration legal-status Critical
Expired - Lifetime legal-status Critical Current

Links

Landscapes

  • Catalysts (AREA)
  • Exhaust Gas Treatment By Means Of Catalyst (AREA)

Description

【発明の詳細な説明】 【0001】 【産業上の利用分野】本発明は、排気ガス浄化用触媒に
関し、さらに詳しくは、酸素過剰下の排気ガス、すなわ
ち、排気ガス中に含まれる一酸化炭素、水素および炭化
水素等の還元性物質を完全に酸化させるのに必要な酸素
量よりも過剰な量の酸素が含まれている排気ガス中のN
Ox(窒素酸化物)を効率よく浄化する排気ガス浄化用触
媒に関する。 【0002】 【従来の技術】従来より、自動車の排気ガス浄化用触媒
として、排気ガス中の一酸化炭素(CO)および炭化水
素(HC)の酸化と、窒素酸化物(NOx )の還元とを
同時に行うことにより排気ガスを浄化する排気ガス浄化
用三元触媒が数多く知られている。このような触媒とし
ては、例えば、コージュライトなどの耐熱性担体にγ−
アルミナスラリーを塗布し、焼成し、Pd、Pt、Rh
などの貴金属を担持させた触媒が典型的である。 【0003】ところで、これら排気ガス浄化用触媒は、
エンジンの設定空燃比によりその性能が大きく左右さ
れ、特に、希薄混合雰囲気、すなわち空燃比の大きいリ
ーン側では、燃焼後の排気ガス中の酸素量が多くなり、
酸化作用が活発に、還元作用が不活発になる。逆に、空
燃比の小さいリッチ側では、燃焼後の排気ガス中の酸素
量が少なくなり、酸化作用が不活発に、還元作用が活発
になる。 【0004】一方、近年、資源問題、地球温暖化の観点
から省エネルギーが求められ、自動車の低燃費化の要請
が強く、ガソリンエンジンにおいては効率的な燃焼面か
ら希薄燃焼(リーンバーン)が注目されている。この希
薄燃料では、通常走行時になるべく酸素過剰の混合気で
燃焼させるリーン側での運転が行われており、リーン側
でも十分にNOx を浄化できる触媒が望まれていた。 【0005】そこで、これら問題を解決するため、この
ような酸素過剰雰囲気下の自動車排気ガス浄化触媒とし
て、一酸化炭素、炭化水素の酸化と窒素酸化物の還元を
同時に行う触媒が種々提案されている。例えば、アルミ
ナ担体に白金を担持させて成るPt/Al2 3 もその
一例であるが、実用上充分な浄化率を示すものではな
く、特に過渡状態時(市街地走行模擬状態時)において
問題がある。 【0006】一方、本出願人等は過渡状態時(市街地走
行模擬状態時)において、NOx浄化率を高めるために
アルミナ担体に白金およびランタン酸化物(La
2 3 )を担持した触媒を提案した(特願平3−344
781)。この触媒は定常走行のような、空燃比A/F
がリーンの状態ではNOxは一部がHCにより還元され
て窒素になり、残りの未反応NOxは触媒中のLa2
3 上に吸着され、車両加速時や車両停止時のA/Fが理
論A/Fの際にはLa2 3 上に吸着されたNOxが浄
化される。 【0007】 【発明が解決しようとする課題】しかしながら、アルミ
ナ担体にPtおよびLa2 3 を担持した触媒には、必
ずしも必要十分な浄化率が得られないという問題があ
る。この理由は必ずしも明確ではないが、リーンA/F
時のLa2 3 のNOxの吸着量や理論A/F時のNO
x の放出速度が不足しているためと推察される。 【0008】従って、本発明の目的は、酸素過剰雰囲気
下において、排気ガス中の一酸化炭素、炭化水素及び窒
素酸化物の浄化効率に優れた排気ガス浄化用触媒を提供
することにある。また、本発明の他の目的は、希薄燃焼
型自動車の走行状態のように、理論空燃比近傍からオー
バーリーン(A/F=約23程度)までの範囲内で頻繁
にガス組成が変化するような使用状態において、排気ガ
ス中の一酸化炭素、炭化水素及び窒素酸化物を共に効率
よく浄化する排気ガス浄化用触媒を提供することにあ
る。 【0009】 【課題を解決するための手段】本発明に従えば、希薄燃
焼エンジンから排出される排気ガス中の一酸化炭素、炭
化水素及び窒素酸化物を同時に浄化する排気ガス浄化用
触媒において、多孔質体からなる担体に(i)白金又は
パラジウム並びに(ii)ランタンと希土類金属及び遷移
金属の中から選ばれた少なくとも1種の金属との格子欠
陥を有する複合酸化物を担持せしめて成り、リーン時に
は窒素酸化物をランタンに吸着せしめ、ストイキ時及び
リッチ時にその窒素酸化物を放出して排気ガスを浄化す
排気ガス浄化用触媒が提供される。 【0010】本発明に係る排気ガス浄化用触媒は、前記
した通り、多孔質体からなる担体に、(i)白金又はパ
ラジウム及びこれらに加えて任意的なロジウム並びに
(ii)ランタンと希土類金属及び遷移金属の中から選ば
れた少なくとも一種の金属との格子欠陥を有する複合酸
化物を担持せしめて成る。本発明において用いることの
できる多孔質担体としては、アルミナ、ゼオライト、ジ
ルコニア、シリカアルミナ、シリカ等をあげることがで
きる。これらの多孔質担体の種類及び物性については特
に限定はなく、従来から触媒用として使用されていた任
意の多孔質担体を使用することができる。また、これら
の多孔質担体はコージュライト、耐熱金属合金等からな
るハニカム基体にコートして用いても良い。 【0011】本発明に係る排気ガス浄化用触媒におい
て、前記した多孔質担体に担持される白金及び/又はパ
ラジウムの担持量には特に限定はないが、一般には多孔
質体1リットル当り0.1〜5g原子、好ましくは0.
5〜2.5g担持される。本発明の好ましい態様では白
金又はパラジウムに加えて、ロジウムを担持させると、
NOx とCO又はHCとの反応が促進されるので好まし
い。好ましいRhの担持量は多孔質体1リットル当り
0.05〜0.5g原子である。 【0012】本発明に係る排気ガス浄化用触媒は、多孔
質担体に更に(a)ランタンと(b)希土類金属(例え
ば、Ce、Pr、Nd、Sm、Eu、Tb)及び/又は
遷移金属(例えば、Co、Mn、Fe、Cr、Ni、C
u)との格子欠陥を有する複合酸化物を担持させる。こ
のような複合酸化物の代表的なものとしては、(Ce
1-X LaX )O3 及び(La1-X CeX )23 (式中、
x=0.01〜 0.5)などのLa−Ce系複合酸化物、La
MO3 及び(La1-X SrX )MO3 (式中、M=C
o、Mn、Fe、Cr)などのLaMO3 型ペロブスカ
イト、La2 MO4及び(La2-X SrX )MO4 (式
中、M=Cu、Ni)などをあげることができる。かか
る複合酸化物の担持量には特に限定はないが、多孔質担
体1リットル当り、好ましくは0.05〜1.0 mol、
更に好ましくは0.2〜0.5 mol担持させるのが良
い。 【0013】本発明に係る排気ガス浄化用触媒は、通
常、多孔質体、好ましくはアルミナ、シリカアルミナ、
ゼオライトに、ランタン及び希土類金属(又は遷移金
属)の水溶性化合物の水溶性を被覆、焼成し、次に、こ
れに白金もしくはパラジウム(又は更にロジウム)の水
溶性化合物の水溶液を被覆、焼成することによって製造
することができる。 【0014】本発明に係る排気ガス浄化用触媒を用いて
排気ガスを浄化するにあたっては、通常の方法で実施す
ることができ、排気ガスを触媒層に導入する空間速度(S
V)にも特に限定はなく、例えば 300,000〜10,000hr-1
範囲が好ましく、また触媒層温度にも特に制限はない
が、 200〜 800℃程度の温度が好ましい。 【0015】 【作用】ランタンとセリウムなどの希土類又はコバルト
などの遷移金属と複合酸化物では、ランタンと例えばセ
リウムとの酸化数が異なるため複合酸化物を形成すると
格子欠陥が生じ、本発明の知見によれば、このような格
子欠陥がNOx の触媒上への吸着、放出作用を促進し、
NOx の浄化率が向上するものと思われる。また、本発
明の触媒を用いれば、二次的な効果として、例えばアル
ミナ担体にPtおよびLa2 3 を担持した従来の触媒
の他の問題点である耐熱性や耐イオウ被毒性も向上させ
ることができる。これは、複合酸化物の生成によりアル
ミナとランタンとの反応を抑制し、さらに生成する硫酸
塩の分解を容易にするためであると考えられる。 【0016】即ち、従来のPt及びLa2 3 をアルミ
ナ担体に担持させた触媒では、アルミナとランタンとの
反応で、LaAlO3 が生成して触媒上でのPtの高分
散状態が損なわれ、またLaのNO吸収作用がなくなる
ため、NOx 浄化率が低下するものと想定されていた
が、本発明ではLaAlO3 の生成が効果的に抑制され
るためにかかる問題が起こらない。本発明によれば、リ
ーン時に、排ガス中のNOやSO2 がLaにとり込まれ
てLa(NO3 3 及びLa2(SO4 3 となる。次に
ストイキ時やリッチ時には、La(NO3 3 が分解し
て、NO2 の放出浄化がおこるが、La2(SO4)3 は分
解せず、触媒上に蓄積していく。ところが本発明ではC
eなどの希土類金属やコバルトなどの遷移金属の存在に
より、La 2(SO4)3 がLaとSO2 とに分解されるの
でLaのNO吸収作用が生じるようになる。なお、この
作用はLaと、希土類金属や遷移金属がそれぞれ単独で
存在していても生ぜず、両者が格子欠陥を有する複合酸
化物の形で存在していることが肝要である。 【0017】 【実施例】以下、実施例によって本発明を更に説明する
が、本発明の範囲をこれらの実施例に限定するものでは
ない。 【0018】例1〜8 担持量の異なる、貴金属(Pt、Pd、Rh)/ランタ
ン・セリウム複合酸化物(又はランタン、コバルト複合
酸化物)/Al2 3 触媒を製造し、性能評価試験を行
った。 〔触媒調製1〕活性アルミナ粉末100重量部にアルミ
ナゾル(アルミナ含有量:10重量%)70重量部、4
0重量%硝酸アルミニウム水溶液15重量部、および水
30重量部を加えて攪拌混合し、コーティング用スラリ
ーを調製した。このコーティング用スラリーを用い、コ
ージェライト製ハニカム担体に常法に従ってアルミナコ
ートを施した。次にこの担体を硝酸ランタンと硝酸セリ
ウムの混合水溶液に浸漬し、乾燥後、650℃で1時間
焼成した。次いで、所定の濃度のジニトロジアンミン白
金水(又は硝酸パラジウム)溶液と硝酸ロジウム混合水
溶液に浸漬し、乾燥後300℃、1時間焼成して表1の
触媒 No.1,2,3及び4(実施例)を得た。尚、比較
のためにランタンのみ又はセリウムのみを担持した触媒
No.6及び7(比較例)も調製した。 【0019】〔触媒調製2〕活性アルミナ粉末100重
量部にアルミナゾル(アルミナ含有量:10重量%)7
0重量部、40重量%硝酸アルミニウム水溶液15重量
部、および水30重量部を加えて攪拌混合し、コーティ
ング用スラリーを調製した。このコーティング用スラリ
ーに(La0.8 、Sr0.2)CoO3 粉末を加え混合攪拌
した。なお、このときの(La0.8 、Sr0.2)CoO3
粉末混合量は、触媒完成時に触媒Iリットル当たり0.
3molの(La0.8 、Sr0.2)CoO3 が担持される
様に調製した。このコーティング用スラリーを用い、コ
ージェライト製ハニカム担体にアルミナコートを施し
た。乾燥後、650℃で1時間焼成した。次いで、所定
の濃度のジニトロジアンミン白金水溶液と硝酸ロジウム
混合水溶液に浸漬し、乾燥後300℃、1時間焼成し
て、表1、触媒 No.5(実施例)を得た。 【0020】 【表1】【0021】〔活性評価〕上で調製した各触媒を希薄燃
焼エンジンの排気系に配置し、エンジンをA/F=22
の条件で運転して定常状態における触媒の浄化率を測定
した。また、過渡状態としてA/F=14.5(ストイ
キ)とA/F=18(リーン)とを6分周期で変化させ
ることにより行った。耐久試験は、入りガス温度700
℃でA/F=14.5とA/F=18を1:9の割合で
10分周期で交互に変化させて、100時間行い、この
後の活性を評価した。結果を表2に示す。表2の結果よ
り明らかなように、本発明の触媒は初期浄化性能及び耐
久浄化性能ともに優れている。 【0022】 【表2】【0023】 【発明の効果】以上説明したように、格子欠陥を有する
複合酸化物を担持させた本発明触媒によれば、LaのN
Oの吸収放出作用を著しく促進することができる。
DETAILED DESCRIPTION OF THE INVENTION [0001] The present invention relates to an exhaust gas purifying catalyst.
More specifically, exhaust gas with excess oxygen,
That is, carbon monoxide, hydrogen and carbon
Oxygen required to completely oxidize reducing substances such as hydrogen
N in exhaust gas containing an excessive amount of oxygen
Exhaust gas purification catalyst that efficiently purifies Ox (nitrogen oxide)
Medium. [0002] 2. Description of the Related Art Conventionally, catalysts for purifying exhaust gas from automobiles have been used.
As carbon monoxide (CO) and hydrocarbons in exhaust gas
Oxidation of nitrogen (HC) and reduction of nitrogen oxides (NOx)
Exhaust gas purification that purifies exhaust gas by performing simultaneously
Many three-way catalysts are known. Such a catalyst
For example, γ-
Alumina slurry is applied and fired, and Pd, Pt, Rh
A catalyst supporting a noble metal such as a noble metal is typical. Incidentally, these exhaust gas purifying catalysts are:
Its performance greatly depends on the set air-fuel ratio of the engine.
In particular, lean mixed atmospheres, that is, those with a large air-fuel ratio
On the other hand, the amount of oxygen in the exhaust gas after combustion increases,
Oxidation is active and reduction is inactive. Conversely, the sky
On the rich side where the fuel ratio is small, the oxygen in the exhaust gas after combustion
Reduced amount, oxidizing action is inactive, reducing action is active
become. On the other hand, in recent years, resource issues and global warming
Demand for energy savings and demand for lower fuel consumption of automobiles
Is a strong and efficient combustion aspect for gasoline engines?
Lean burn has attracted attention. This rare
With thin fuel, use a mixture of oxygen excess as much as possible during normal driving.
The operation on the lean side to burn is performed, and the lean side
However, a catalyst that can sufficiently purify NOx has been desired. [0005] To solve these problems,
Catalyst for purifying automobile exhaust gas under such an oxygen-rich atmosphere
To oxidize carbon monoxide and hydrocarbons and reduce nitrogen oxides.
Various catalysts to be performed simultaneously have been proposed. For example, aluminum
Pt / Al with platinum supported on carrierTwoOThreeAlso
This is an example, but it does not show a sufficient purification rate for practical use.
Especially in the transient state (simulated city driving)
There's a problem. [0006] On the other hand, the present applicant and the like in the transition state (city driving)
To improve the NOx purification rate in the simulation mode)
Platinum and lanthanum oxide (La
TwoOThree(Japanese Patent Application No. 3-344).
781). This catalyst has an air-fuel ratio A / F as in a steady running.
Is lean, NOx is partially reduced by HC
And the remaining unreacted NOx becomes La in the catalyst.TwoO
ThreeA / F during vehicle acceleration and vehicle stoppage
In the case of A / F, LaTwoOThreeNOx adsorbed on the top is purified
Be converted to [0007] SUMMARY OF THE INVENTION However, aluminum
Pt and La on carrierTwoOThreeIs required for catalysts carrying
There is a problem that a sufficient and sufficient purification rate cannot be obtained.
You. The reason is not always clear, but lean A / F
La at timeTwoOThreeNOx adsorption amount and NO at theoretical A / F
It is presumed that the release speed of x was insufficient. Accordingly, an object of the present invention is to provide an oxygen-excess atmosphere
Below, carbon monoxide, hydrocarbons and nitrogen in the exhaust gas
Providing an Exhaust Gas Purification Catalyst with Excellent Oxide Purification Efficiency
Is to do. Another object of the present invention is to provide a lean burn
From the vicinity of the stoichiometric air-fuel ratio
Frequent within the range up to burlean (A / F = about 23)
Exhaust gas in a usage condition where the gas composition changes
Efficiency of carbon monoxide, hydrocarbons and nitrogen oxides in gas
To provide an exhaust gas purification catalyst that purifies well
You. [0009] According to the present invention,Lean burn
Emitted from the burning engineCarbon monoxide and charcoal in exhaust gas
Exhaust gas purification for simultaneous purification of hydrogen hydride and nitrogen oxides
In the catalyst, (i) platinum or
Palladium and (ii) lanthanum and rare earth metals and transitions
Lack of lattice with at least one metal selected from metals
The composite oxide withWhen lean
Makes nitrogen oxides adsorb on lanthanum,
Purifies exhaust gas by releasing its nitrogen oxides when rich
ToAn exhaust gas purification catalyst is provided. The exhaust gas purifying catalyst according to the present invention is characterized in that
As described above, (i) platinum or
Radium and in addition to these optional rhodium and
(Ii) Lanthanum, selected from rare earth metals and transition metals
Complex acid having lattice defect with at least one selected metal
On the substrate. Of the present invention
Porous carriers that can be used include alumina, zeolite,
Luconia, silica alumina, silica, etc.
Wear. Regarding the types and physical properties of these porous carriers,
There is no limitation on the
Any porous carrier can be used. Also these
The porous carrier is made of cordierite, heat-resistant metal alloy, etc.
May be used after being coated on a honeycomb substrate. The catalyst for purifying exhaust gas according to the present invention
And the platinum and / or palladium supported on the porous carrier described above.
The amount of supported radium is not particularly limited, but is generally porous.
0.1 to 5 g atoms, preferably 0.1 to 0.5 g atoms per liter of the solid body.
5 to 2.5 g are carried. In a preferred embodiment of the invention, white
In addition to gold or palladium, when carrying rhodium,
It is preferable because the reaction between NOx and CO or HC is promoted.
No. The preferred amount of supported Rh is per liter of the porous body.
0.05-0.5 g atom. The exhaust gas purifying catalyst according to the present invention has a porous structure.
(A) lanthanum and (b) rare earth metal (for example,
For example, Ce, Pr, Nd, Sm, Eu, Tb) and / or
Transition metals (eg, Co, Mn, Fe, Cr, Ni, C
A composite oxide having a lattice defect with u) is supported. This
Typical examples of composite oxides such as (Ce
1-XLaX) OThreeAnd (La1-XCeX)TwoOThree(Where
x = 0.01-0.5) La-Ce based composite oxide, La
MOThreeAnd (La1-XSrX) MOThree(Where M = C
o, Mn, Fe, Cr)ThreeType perovska
It, LaTwoMOFourAnd (La2-XSrX) MOFour(formula
And M = Cu, Ni). Heel
There is no particular limitation on the loading amount of the composite oxide,
Preferably 0.05 to 1.0 mol per liter of body,
More preferably, 0.2 to 0.5 mol is supported.
No. [0013] The exhaust gas purifying catalyst according to the present invention is generally used.
Usually, a porous body, preferably alumina, silica alumina,
Lanthanum and rare earth metals (or transition gold)
The water-soluble compound of the genus) is coated and calcined, and then
Platinum or palladium (or even rhodium) water
Manufactured by coating and baking an aqueous solution of a soluble compound
can do. Using the catalyst for purifying exhaust gas according to the present invention
When purifying exhaust gas, use a normal method.
The space velocity (S
V) is not particularly limited, for example, 300,000 to 10,000 hr.-1of
The range is preferable, and the catalyst layer temperature is not particularly limited.
However, a temperature of about 200 to 800 ° C is preferable. [0015] [Function] Lanthanum and rare earth such as cerium or cobalt
Lanthanum and complex oxides
When the composite oxide is formed due to the different oxidation number with helium
Lattice defects occur, and according to the knowledge of the present invention, such cases
Child defects promote NOx adsorption and release on the catalyst,
It is thought that the purification rate of NOx is improved. In addition,
The use of bright catalysts has a secondary effect, for example,
Pt and La on Mina carrierTwoOThreeConventional catalyst loaded with
It also improves the other problems of heat resistance and sulfur poisoning.
Can be This is due to the formation of composite oxides.
Sulfuric acid that suppresses the reaction between mina and lanthanum and further forms
This is considered to be to facilitate the decomposition of the salt. That is, conventional Pt and LaTwoOThreeThe aluminum
In a catalyst supported on a carrier, alumina and lanthanum
In reaction, LaAlOThreeIs generated and the Pt concentration on the catalyst increases.
Dispersion state is impaired and La NO absorption effect is lost
Therefore, it was assumed that the NOx purification rate would decrease.
However, in the present invention, LaAlOThreeGeneration is effectively suppressed
Such a problem does not occur. According to the present invention,
NO and SO in exhaust gasTwoIs taken into La
La (NOThree)ThreeAnd LaTwo(SOFour)ThreeBecomes next
At the time of stoichiometry or rich, La (NOThree)ThreeBreaks down
And NOTwoEmission purification occurs, but LaTwo(SOFour)ThreeIs a minute
Without understanding, it accumulates on the catalyst. However, in the present invention, C
e and rare earth metals and transition metals such as cobalt
Than La Two(SOFour)ThreeIs La and SOTwoWill be broken down into
Then, the NO absorption effect of La comes to occur. Note that this
The action is La and rare earth metal and transition metal are each independently
A complex acid that does not occur even if it exists and both have lattice defects
It is important that they exist in the form of chloride. [0017] The present invention will be further described with reference to the following examples.
However, the scope of the present invention is not limited to these examples.
Absent. [0018]Examples 1 to 8 Precious metals (Pt, Pd, Rh) / Lanta with different loading amounts
Cerium composite oxide (or lanthanum, cobalt composite
Oxide) / AlTwoOThreeManufacture catalysts and conduct performance evaluation tests
Was. [Catalyst preparation 1] Aluminum was added to 100 parts by weight of activated alumina powder.
70 parts by weight of Nasol (alumina content: 10% by weight), 4
15 parts by weight of 0% by weight aqueous aluminum nitrate solution and water
Add 30 parts by weight, stir and mix, slurry for coating
Was prepared. Using this coating slurry,
-Alumina coated on a jellyite honeycomb carrier
Was applied. Next, the carrier was lanthanum nitrate and cellulose nitrate
650 ° C for 1 hour
Fired. Then, a predetermined concentration of dinitrodiammine white
Gold water (or palladium nitrate) solution and rhodium nitrate mixed water
After immersion in a solution, drying and baking for 1 hour at 300 ° C.,
Catalyst Nos. 1, 2, 3, and 4 (Examples) were obtained. In addition, comparison
Supported only lanthanum or only cerium
 Nos. 6 and 7 (Comparative Examples) were also prepared. [Catalyst preparation 2] 100 weights of activated alumina powder
Alumina sol (alumina content: 10% by weight)
0 parts by weight, 15% by weight of 40% by weight aqueous solution of aluminum nitrate
And 30 parts by weight of water, and stir and mix.
A slurry for polishing was prepared. This coating slurry
-(La0.8, Sr0.2) CoOThreeAdd powder and stir
did. At this time, (La0.8, Sr0.2) CoOThree
The mixing amount of the powder was set at 0.
3 mol of (La0.8, Sr0.2) CoOThreeIs carried
Prepared in the same manner. Using this coating slurry,
-Alumina coated on honeycomb carrier made of gelite
Was. After drying, baking was performed at 650 ° C. for 1 hour. Then, predetermined
Dinitrodiammine platinum aqueous solution and rhodium nitrate at different concentrations
After immersion in a mixed aqueous solution, drying and baking at 300 ° C for 1 hour
Thus, Table 1, Catalyst No. 5 (Example) was obtained. [0020] [Table 1][Evaluation of activity] Each of the catalysts prepared above
A / F = 22 placed in the exhaust system of the firing engine
Operating under the above conditions and measuring the purification rate of the catalyst in the steady state
did. Also, as a transient state, A / F = 14.5 (stoichiometry)
G) and A / F = 18 (lean) at 6-minute intervals
It was done by doing. The endurance test was performed with the gas temperature 700
At A / F = 14.5 and A / F = 18 at a ratio of 1: 9
Performed for 100 hours, alternating with a 10 minute cycle,
Later activity was evaluated. Table 2 shows the results. Table 2 shows the results.
As is clear, the catalyst of the present invention has an initial purification performance and
Excellent purification performance. [0022] [Table 2][0023] As described above, it has lattice defects.
According to the catalyst of the present invention supporting a composite oxide, N of La
The absorption and release action of O can be remarkably promoted.

フロントページの続き (56)参考文献 特開 平2−218439(JP,A) 特開 平4−27435(JP,A) 特開 昭57−63133(JP,A) 特開 昭63−77543(JP,A) 特開 平5−220395(JP,A) 特開 平6−262040(JP,A) (58)調査した分野(Int.Cl.7,DB名) B01J 21/00 - 37/36 B01D 53/86 F01N 3/28 Continuation of the front page (56) References JP-A-2-218439 (JP, A) JP-A-4-27435 (JP, A) JP-A-57-63133 (JP, A) JP-A-63-77543 (JP) JP-A-5-220395 (JP, A) JP-A-6-262040 (JP, A) (58) Fields investigated (Int. Cl. 7 , DB name) B01J 21/00-37/36 B01D 53/86 F01N 3/28

Claims (1)

(57)【特許請求の範囲】 【請求項1】 希薄燃焼エンジンから排出される排気ガ
ス中の一酸化炭素、炭化水素及び窒素酸化物を同時に浄
化する排気ガス浄化用触媒において、多孔質体からなる
担体に(i)白金又はパラジウム並びに(ii)ランタン
と希土類金属及び遷移金属の中から選ばれた少なくとも
1種の金属との格子欠陥を有する複合酸化物を担持せし
めて成り、リーン時には窒素酸化物をランタンに吸着せ
しめ、ストイキ時及びリッチ時にその窒素酸化物を放出
して排気ガスを浄化する排気ガス浄化用触媒。
(1) An exhaust gas purifying catalyst for simultaneously purifying carbon monoxide, hydrocarbons and nitrogen oxides in exhaust gas discharged from a lean burn engine. to become a carrier (i) platinum or palladium and (ii) lanthanum and rare earth Ri metal and formed by allowed carrying a composite oxide having a lattice defect and at least one metal selected from among transition metals, nitrogen during lean Adsorb oxide on lanthanum
Releases nitrogen oxides during stoichiometric and rich conditions
Exhaust gas purification catalyst that purifies exhaust gas.
JP00249293A 1993-01-11 1993-01-11 Exhaust gas purification catalyst Expired - Lifetime JP3379125B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP00249293A JP3379125B2 (en) 1993-01-11 1993-01-11 Exhaust gas purification catalyst

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP00249293A JP3379125B2 (en) 1993-01-11 1993-01-11 Exhaust gas purification catalyst

Publications (2)

Publication Number Publication Date
JPH06205975A JPH06205975A (en) 1994-07-26
JP3379125B2 true JP3379125B2 (en) 2003-02-17

Family

ID=11530866

Family Applications (1)

Application Number Title Priority Date Filing Date
JP00249293A Expired - Lifetime JP3379125B2 (en) 1993-01-11 1993-01-11 Exhaust gas purification catalyst

Country Status (1)

Country Link
JP (1) JP3379125B2 (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN100341606C (en) * 2005-06-20 2007-10-10 天津化工研究设计院 Double functional deoxidation agent and production process thereof

Families Citing this family (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US8530372B2 (en) 2009-07-22 2013-09-10 Basf Corporation Oxygen storage catalyst with decreased ceria reduction temperature

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN100341606C (en) * 2005-06-20 2007-10-10 天津化工研究设计院 Double functional deoxidation agent and production process thereof

Also Published As

Publication number Publication date
JPH06205975A (en) 1994-07-26

Similar Documents

Publication Publication Date Title
EP0852966B1 (en) Exhaust gas purifying catalyst and exhaust gas purifying method
JP3291086B2 (en) Exhaust gas purification catalyst and exhaust gas purification method
JP3311012B2 (en) Exhaust gas purification catalyst and exhaust gas purification method
JPH07232064A (en) Catalyst for purification of exhaust gas
JP3965676B2 (en) Exhaust gas purification catalyst and exhaust gas purification system
EP0589393B1 (en) Method for purifying oxygen rich exhaust gas
US7384889B2 (en) Exhaust gas purifying catalyst and exhaust gas purifying system
JP3685463B2 (en) Exhaust gas purification catalyst
JPH08281106A (en) Catalyst for purifying exhaust gas and its production
JPH09253453A (en) Cleaning of exhaust gas
JPH0810573A (en) Exhaust gas purifying device
JPH09220470A (en) Catalyst for purification of exhaust gas
JPH10192713A (en) Exhaust gas purifying catalyst and its use
JP3379125B2 (en) Exhaust gas purification catalyst
JPH10165819A (en) Catalyst for cleaning of exhaust gas and its use method
JPH1157477A (en) Exhaust gas cleaning catalyst and method of using the same
JP3395525B2 (en) Internal combustion engine exhaust gas purification catalyst and purification method
JP3320855B2 (en) Exhaust gas purification method
JPH0871424A (en) Catalyst for purification of exhaust gas
JP4019351B2 (en) NOx purification catalyst and NOx purification system
JP3477982B2 (en) Exhaust gas purification catalyst and exhaust gas purification method
JP3391569B2 (en) Exhaust gas purification method
JP2745644B2 (en) Exhaust gas purification catalyst
JPH11294150A (en) Exhaust emission control device and its use
JP3723151B2 (en) Exhaust gas purification method

Legal Events

Date Code Title Description
FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20081213

Year of fee payment: 6

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20081213

Year of fee payment: 6

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20091213

Year of fee payment: 7

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20101213

Year of fee payment: 8

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20101213

Year of fee payment: 8

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20111213

Year of fee payment: 9

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20111213

Year of fee payment: 9

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20121213

Year of fee payment: 10

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20131213

Year of fee payment: 11

EXPY Cancellation because of completion of term
FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20131213

Year of fee payment: 11